• Application Note

High Throughput Determination of Emerging Synthetic Amphetamine Drugs in Untreated Wastewater Using SPE-LC-MS/MS

High Throughput Determination of Emerging Synthetic Amphetamine Drugs in Untreated Wastewater Using SPE-LC-MS/MS

Vishnu Cheerala1, Ghenwa Hafez1, Bhaskar K1, Raghu Tadala1, Dnyaneshwar Shinde1, Dr Parth Gupta1, Dr Wael Elamin1, Dr. Grzegorz Brudecki1, Samara Bin Salem2, P.M.N. Rajesh3, Jesus Gomez-Mares3

RASID ADQCC – operated by M42, Abu Dhabi, UAE

Abu Dhabi Quality and Conformity Council, Abu Dhabi, UAE

Waters Corporation, United States

Published on July 16, 2025


Abstract

Sewage-based epidemiology (SBE) is a pioneering approach utilizing sewage samples to detect and quantify illicit drugs usage trends within a community. While SBE has been traditionally applied to estimate the prevalence of conventional illicit drugs since 2005, there has only been limited exploration on the detection of new psychoactive substances (NPS) in untreated wastewater samples. These substances mimic the effects of illicit drugs with the introduction of subtle modifications to the chemical structures of controlled illicit drugs. Identifying and determining these NPS poses challenges for government control bodies due to the evolving nature of their production, while presenting a pressing concern.

In this study, we present a new analytical method employing liquid chromatography coupled to positive electrospray ionization tandem quadrupole mass spectrometry (LC-ESI-MS/MS) for the determination of 18 emerging amphetamine NPS in sewage wastewater samples. These substances include methoxetamines (MXE, MBDB, MDA, MDEA, MDMA, MDPV), Butylone, methylone, 4-methoxyamphetamine (PMA), 1,3-Benzodioxolyl butamine (BDB), 4-Bromo-2,5-Dimethoxy phenethylamine (2C-B), and 2,5-Dimethoxy-4-iodo phenethylamine (2C-I), among others.

Sample preparation involved solid-phase extraction (SPE) utilizing an Oasis™ MCX LP 96 Well Plate. The LC separation was achieved using an ACQUITY™ Premier BEH™ C18 Column (1.7 µm, 2.1 x 100 mm), ensuring optimal resolution of analytes within a total runtime of 12 minutes. The limits of quantification (LOQ) ranged between 0.033–300.0 µl/L for all compounds on the Xevo™ TQ-XS Tandem Quadrupole Mass Spectrometer. Method validation encompassed sensitivity, specificity, linearity, accuracy, precision, recoveries, and matrix effects.

Benefits

  • Lower untreated wastewater sample processing volumes and simplified analytical workflows resulted in quicker analysis times and the potential for high sample throughput
  • In-house method validation demonstrated the performance of the method and its ease of implementation
  • Method is suitable for high throughput analysis of 18 different amphetamine drugs in untreated wastewater to check compliance against regulatory limits

Introduction

The rapid emergence of numerous new psychoactive substances (NPS) known as legal highs, designer drugs, or bath salts synthacaines in the illegal drug market poses significant risk to public health and challenges drug policy creation.1,2,3 While traditional illicit drugs (e.g., cannabis, cocaine, heroin, ecstasy) continue to dominate the market, the significant rise in the variety of NPS with largely unknown toxicological effects and social harm warrants increased vigilance. Continuous monitoring, information sharing, early warning and risk awareness are essential to respond to the emerging NPS. A large portion of these NPS comprise various amphetamine-like substances, including synthetic cathinones and sympathomimetic amines which are designed to replicate the pharmacological effects of the original drugs. Demand is increasing for the analysis and identification of a large number of chemically diverse substances present in drug markets in different sample matrices.4,5,6

The quantification of drugs of abuse (DOA) in aquatic habitats has grown in popularity in recent years due to advantages such as their sample collection being a non-invasive technique of larger sample volumes with no legal concerns. Quantitative examination of untreated wastewater provides significant data for estimating drug consumption at local and national levels, as well as providing insights through comparison against international data. Routine monitoring can establish an early warning system for the government bodies. This approach is a viable path for epidemiological research on illegal drug use and addiction, as it provides real-time, evidence-based insights that supplement survey-based studies.

Accurate and reliable methods with the lowest possible LOQ are essential for monitoring untreated wastewater samples to understand the prevalence of these compounds and assess their temporal variability.This study aims to develop and validate a high-throughput, multi-residue chromatographic method for the detection of 18 synthetic amphetamine designer drugs at the possible LOQ in untreated wastewater samples. The method focuses on synthetic cathinones and other substituted phenylalkylamines, providing a tool for early detection of these compounds in urban communities as part of drug abuse mitigation efforts, as well as studying their occurrence and fate in aquatic environments.1

Experimental

Calibration Standards and Sample Preparation

An analytical standard mix of 18 amphetamine analog drugs was used to prepare an intermediate working solution. This was then used to create 8 calibration standards and three QC standards at different levels independent of the calibration concentrations in untreated wastewater matrix. The calibration standards were prepared over the range of 0.033 to 300 µg/L. An internal standard mix was prepared and added before sample extraction.

Untreated wastewater samples were screened and stored at 4 °C. For analysis, aliquots (5 mL) were transferred to 15 mL centrifuge tubes, spiked with the internal standard mix and acidified. Before loading the samples onto the SPE 96 well plate, they were vortexed. The detailed extraction protocol is shown in Figure 1.

SPE workflow to extract Amphetamines from untreated wastewater
Figure 1. SPE workflow to extract Amphetamines from untreated wastewater.

LC Conditions

LC system:

ACQUITY UPLC I-Class Plus System with BSM and FTN SM

96-well collection plate:

Polypropylene 2 mL Square Collection Plate (p/n: 186002482)

Column:

ACQUITY Premier BEH C18 (1.7 µm, 2.1 x 100 mm) (p/n: 186009453)

Column temperature:

55 °C

Sample temperature:

10 °C

Injection volume:

5 µL

Mobile phase A:

0.5 mM ammonium acetate with 0.025% acetic acid in water

Mobile phase B:

methanol:acetonitrile (70:30 v/v) with 0.025% acetic acid

Gradient Table

Gradient Table

MS Conditions

MS system:

Xevo TQ-XS

Ionization mode:

Electrospray (positive ion mode)

Capillary voltage:

1.2 kV

Source temperature:

150 °C

Disolvation temperature:

600 °C

Disolvation gas flow:

1000 L/hr

Cone gas flow:

150 L/hr

Data Management

MS acquisition software:

MassLynx™ 4.2 Software

Quantitation software:

TargetLynx™ 4.2 Software

Method Validation

Single laboratory validation was performed by replicate analysis of spiked, screened blank, untreated wastewater samples. The following performance factors were assessed: specificity, sensitivity, calibration graph characteristics, trueness (% recovery), repeatability (RSDr), and within-laboratory reproducibility (RSDip), also called intermediate precision. Trueness and RSDip were determined from replicate analysis (n=18) of spiked samples prepared at three QC levels HQC, MQC, and LQC in screened, untreated wastewater matrix and analyzed on three different days.

Results and Discussion

Chromatography and Sensitivity

The method provided excellent chromatographic retention and peak shape for all the amphetamine drugs. Average retention time and %RSD in untreated wastewater (n=42) are summarized in Table 1 with excellent retention time reproducibility observed and all %RSDs <0.21. Figure 2 shows typical total ion chromatograms (TIC) for all 18 amphetamine analogs, from the analysis of untreated wastewater samples spiked at the LOQ level. The observable peak shapes and signal-to-noise ratios demonstrate that the high throughput method can quantify these analytes in a complex untreated wastewater matrix at low concentrations. Typical TICs of the isotope labelled internal standards in untreated wastewater are shown in Figure 3.

Retention performance of the amphetamines with optimized MRM transitions on the XEVO TQ-XS
Table 1. Retention performance of the amphetamines with optimized MRM transitions on the XEVO TQ-XS.
Typical total ion chromatograms of all 18 amphetamine analogs from the analysis of untreated wastewater samples spiked at LOQ level
Figure 2. Typical total ion chromatograms of all 18 amphetamine analogs from the analysis of untreated wastewater samples spiked at LOQ level.
Typical total ion chromatograms of all 17 Internal standards, from the analysis of raw wastewater samples
Figure 3. Typical total ion chromatograms of all 17 Internal standards, from the analysis of raw wastewater samples. Note: MDA-d5 is used as ISTD for PMA.

Specificity, Identification, and Calibration Criteria

Untreated wastewater was screened and used as matrix blank to check the specificity of the method. No signal was detected in the blanks that could potentially lead to false reporting of non-compliant samples or impact the sensitivity of the method. The ion ratios and the respective retention times of each analyte were within the tolerances given in the ISO 21253–1:2019 standard (part 1).8-point calibration curves were acquired on each day after SPE sample extraction. Linear fit with 1/X2 weighing was applied and all correlation of determination (R2) values were >0.99, with deviation from back calculated concentrations below 15%. Examples of typical calibration curves are given in Figure 4.

Calibration graphs of exemplary amphetamines in untreated wastewater
Figure 4. Calibration graphs of exemplary amphetamines in untreated wastewater.

Laboratory Validation Results

Validation is crucial in analytical chemistry to evaluate the performance characteristics of an analytical method. Within-laboratory validation ensures that a method is fit for its intended purpose. The validation results demonstrated good accuracy for the quantification of all 18 compounds in untreated wastewater (Table 2). The accuracy was determined from the measured values of concentration in the spiked samples, after adjustment using the appropriate internal standard, Trueness, determined as measured mean %recovery (RSDr) between 93.3 to 111.7% and within laboratory precision (RSDwr) between 1.97 and 11.8%. These values are within the acceptance criteria when using internal standards: “yield” (measured recovery) between 70 and 120% and intermediate precision (RSDip) ≤20%. Figure 5 shows a summary of the mean measured recovery values, with associated repeatability.

Summary of the results from the laboratory validation study
Table 2. Summary of the results from the laboratory validation study.
Overview of the mean measured recovery values at LQC, MQC, and HQC
Figure 5. Overview of the mean measured recovery values at LQC, MQC, and HQC spiking levels (according to calibration range given in Table 2) in wastewater sample, with associated repeatability displayed in error bars.

Conclusion

Advancements in public health surveillance increasingly rely on robust, real-time data from unconventional sources like untreated wastewater. A newly developed inhouse analytical method now enables fast, sensitive, and high-throughput detection of 18 synthetic amphetamine analogs, marking a major step forward in wastewater-based epidemiology.

This innovative workflow involves injecting SPE-extracted untreated wastewater samples analysed on a Xevo TQ-XS tandem quadrupole mass spectrometer operated in positive ESI mode coupled to an ACQUITY Premier UPLC I-Class Plus System equipped with a ACQUITY BEH C18 Column. By automation we simplified the sample treatment process and reduced labour-intensive preparation. This method transforms routine testing into a faster and more scalable operation when compare with traditional methods.

Validated according to ISO 17025 and EPA guidelines, the method reliably detects compounds at concentrations as low as 0.033 µg/L using just 5 mL of sample volume. Its design enables high-throughput analysis of up to 100 samples per day, making it highly suitable for real-time public health monitoring and regulatory compliance.

The novelty of this method lies not only in its sensitivity and minimal sample volume but also in its operational efficiency. By integrating automated streamlined sample preparation with tandem mass spectrometry, it significantly enhances lab productivity while maintaining analytical integrity. This makes it particularly valuable for large-scale studies on human drug exposure and temporal trend analysis across urban populations.

This approach demonstrates how environmental monitoring can be both efficient and insightful — delivering near-real-time data that supports public health responses, urban drug policy, and environmental safety with unprecedented speed and accuracy.

References

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  2. Senta, Ivan, et al. “Multiresidual Analysis of Emerging Amphetamine-like Psychoactive Substances in Wastewater and River Water.” Journal of Chromatography A, vol. 1425, 18 Dec. 2015, pp. 204–212, https://doi.org/10.1016/j.chroma.2015.11.043. Accessed 28 Apr. 2023.
  3. Deslandes, Guillaume, et al. ““Synthacaines”: A Mosaic of Substances for a Wide Range of Effects, from a Case.” Toxicologie Analytique et Clinique, vol. 29, no. 1, Feb. 2017, pp. 134–138, https://doi.org/10.1016/j.toxac.2017.01.003. Accessed 12 Feb. 2023.
  4. Swortwood, Madeleine J., et al. “Determination of 32 Cathinone Derivatives and Other Designer Drugs in Serum by Comprehensive LC-QQQ-MS/MS Analysis.” Analytical and Bioanalytical Chemistry, vol. 405, no. 4, 23 Nov. 2012, pp. 1383–1397, https://doi.org/10.1007/s00216-012-6548-8.
  5. Wang, Xin, et al. “Targeted Analysis of 116 Drugs in Hair by UHPLC-MS/MS and Its Application to Forensic Cases.” Drug Testing and Analysis, vol. 9, no. 8, 22 Dec. 2016, pp. 1137–1151, onlinelibrary.wiley.com/doi/full/10.1002/dta.2130, https://doi.org/10.1002/dta.2130.
  6. Castiglioni, Sara, et al. “Testing Wastewater to Detect Illicit Drugs: State of the Art, Potential and Research Needs.” Science of the Total Environment, vol. 487, no. 24963530, July 2014, pp. 613–620, https://doi.org/10.1016/j.scitotenv.2013.10.034. Accessed 3 May 2021.
  7. Water Quality—Multi-compound Class Methods—Part 1: Criteria for the Identification of Target Compounds by Gas and Liquid Chromatography and Mass Spectrometry https://cdn.standards.iteh.ai/samples/70256/7831252860754108a7b953863918c846/ISO-21253-1-2019.pdf.

720008736, July 2025

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